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Lake Vermilion Water Quality Assessment

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Lake Vermilion Water Quality Assessment Lake Vermilion (ID #69-0378) St. Louis County, Minnesota LAKE ASSESSMENT PROGRAM 2000 Minnesota Pollution Control Agency Environmental Outcomes Division in cooperation with Minnesota Department of Natural Resources Boise Fort Band of Chippewa University of Minnesota-Duluth Natural Resources Research Institute Sportsman’s Club of Lake Vermilion St. Louis County May 2001 LAKE ASSESSMENT PROGRAM 2000 Lake Vermilion (ID #69-0378) St. Louis County, Minnesota Minnesota Pollution Control Agency Environmental Outcomes Division Jesse Anderson & Steve Heiskary With contributions from Minnesota Department of Natural Resources Duane Williams & Joe Geis Boise Fort Band of Chippewa Les Connor University of Minnesota-Duluth Natural Resources Research Institute Dr. John Kingston Sportsman’s Club of Lake Vermilion Willis Irons, President St. Louis County Mark Johnson & Mark Lindhorst May 2001 Printed on recycled paper containing at least 10 percent fibers from paper recycled by consumers. This material may be made available in other formats, including Braille, large format and audiotape. Table of Contents 1. Summary and Recommendations.................................................................................... 1 2. Background: Description of the Lake Vermilion Watershed.......................................... 6 3. Historical Studies Conducted on Lake Vermilion........................................................... 11 4. In-Lake Conditions, 2000................................................................................................ 16 5. Trophic Status and Summary .......................................................................................... 22 6. Water Quality Trends, Historical Data Summary ........................................................... 27 7. Modeling Summary......................................................................................................... 28 8. Model Review and Goal Setting ..................................................................................... 36 9. References………………………………………………………………………………38 10. Appendices……………………………………………………………………………...40 List of Tables 1. Lake morphometry and watershed areas......................................................................... 7 2. Lake Vermilion summer-mean water quality for summer 2000..................................... 23 3. Lake Vermilion historical data summary........................................................................ 27 4. MINLEAP model results................................................................................................. 31 5. Comparison of observed and predicted values from BATHTUB model........................ 32 6. BATHTUB estimated phosphorus loading to Lake Vermilion....................................... 33 7. Lake Vermilion summer-mean phosphorus and model estimates .................................. 37 List of Figures 1. Location and ecoregion map for Lake Vermilion ........................................................... 6 2. Lake Vermilion watershed map ...................................................................................... 8 3. Lake Vermilion water level record.................................................................................. 10 4. Lake Vermilion sampling sites........................................................................................ 15 5. Dissolved oxygen and temperature profiles for selected sites ........................................ 16 6. Lake Vermilion total phosphorus concentrations............................................................ 17 7. Lake Vermilion chlorophyll-a concentrations, CLMP Data ........................................... 18 8. Dominant algal forms...................................................................................................... 19 9. Select CLMP Secchi data for 2000……………………………………………………...21 10. Carlson’s Trophic Status Index values............................................................................ 24 11. Long-term CLMP Secchi data......................................................................................... 27 12. DNR Large Lakes Program August TP and chlorophyll-a measurements ..................... 29 13. Estimated water and phosphorus loading to Lake Vermilion ......................................... 35 i SUMMARY AND RECOMMENDATIONS Lake Vermilion is the 7th largest lake in Minnesota (40,557 acres) located in St. Louis County, near Tower Minnesota (Figure 1). Land use in the watershed is characterized by forested and wetland uses which is typical for lakes in this region of the state - the Northern Lakes and Forests ecoregion. Lake Vermilion was sampled during the summer of 2000 by Minnesota Pollution Control Agency (MPCA) and University of Minnesota staff, after consultation with the Minnesota Department of Natural Resources (DNR), St. Louis County, and the Sportsman’s Club of Lake Vermilion (Club). The primary focus of this assessment was to evaluate trophic status and nutrient-related trends. Four sites, consistent with historical studies on the lake, were sampled: Pike Bay, Big Bay, Wakemup Bay, and the outlet of the lake. These sites allowed us to begin to look at spatial differences in the quality of the lake and derive meaningful estimates of “mean” condition for the overall lake. Water quality data collected during the study reveal an area-weighted summer mean phosphorus concentration of 23 µg/L, mean chlorophyll-a of 6.3 µg/L, and Secchi transparency of 7 feet (2.5 meters). The phosphorus, chlorophyll-a, and Secchi values are on the upper range of values exhibited by reference lakes in this ecoregion. Total phosphorus, chlorophyll-a, and Secchi transparency help to characterize the trophic status of a lake and in general we see good correspondence between these variables as compared to empirical models (Carlson’s Trophic State Index). For Lake Vermilion, these measures indicate mesotrophic conditions. Historical Citizen Lake-Monitoring Program (CLMP) Secchi transparency data, which date back to 1976, reveal a significant improvement in transparency based on 21 summers of data. During this period, the summer mean Secchi ranged from 5 feet to 9 feet (1.5 – 2.7 m). Transparency varies from year to year, with values near 5 feet in the late 1970’s to 8 feet in the late 1990’s. DNR monitoring (Large Lakes Program) of several sites in August of each year, since the mid 1980’s, did not reveal any significant temporal trends but indicated that TP typically ranges between 20 - 40 µg/L and chlorophyll-a typically ranges between 10 - 20 µg/L during late summer. Two eutrophication models were used to estimate the water quality of Lake Vermillion based on lake and watershed characteristics. These models provided an opportunity to: compare observed measures with predicted, estimate water and phosphorus (P) budgets for the lake, and a further basis for evaluating the quality of the lake. The first model, MINLEAP, provides estimates of in-lake P based on the volume of the lake, size of watershed , and ecoregion characteristics. For Pike Bay, the model predicted an in-lake P of 33 ± 7 µg/L which compared favorably with the observed value (29 µg/L); while for the lake as whole, the model estimated a concentration of 17 ± 5 µg/L which is slightly lower, but not significantly different, than the observed values. This implies that the P concentration in Pike Bay and the overall lake is in the range expected based on the noted characteristics. Other comparisons of predicted and observed chlorophyll-a and Secchi transparency also exhibited reasonable agreement. The second model, BATHTUB, allowed us to “route” water and P-loads through the main basins and estimate water and nutrient budgets for the lake. Pike Bay, which accounts for about one percent of the volume of the lake, has 56 percent of total watershed area of the entire lake draining to it via the Pike and East and West Twin Rivers. This results in high nutrient loading to the Bay, 1 and combined with its shallowness, results in higher TP (29 µg/L) and higher chlorophyll-a (9.5 µg/L) as compared to sites in the main basin of the lake. Internal recycling of TP from the sediments may contribute to the nutrient loading of the Bay as well. Crude estimates of on-site septic system leaching to the lake suggest that this source-category may contribute on the order of five percent of the lake’s P budget. The City of Tower’s wastewater treatment facility was estimated to contribute about three percent of the P loading to Pike Bay. Because of the lakes’ large surface area, atmospheric deposition on the surface of the lake could account for on the order of 15 percent of the P-loading to the lake. Other sources of P loading include direct runoff from the immediate watershed and processes in the lake which encourage re-circulation of phosphorus. Water residence time ranges from about 0.1 year in Pike Bay to about 10.5 years in Wakemup Bay and averages about 4.4 years overall. The combination of observed data and model predictions provide a basis for some initial goal setting for the lake. It is clear that Pike Bay cannot attain the same water quality as that of the main lake because of its shallowness and the large watershed that drains to it. Based on observed and predicted data, a phosphorus goal on the order of 20 to 25 µg/L may be appropriate for the Bay. A slightly lower goal of 15 to 20 µg/L may be appropriate for the main basin of the lake. Further monitoring and more detail modeling of this system will
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